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Pinus virginiana Mill.Virginia scrub pine; Jersey pine; Virginia pine |
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Typical stand of P. virginiana in Uwharrie National Forest, North Carolina. These trees are about 30 cm dbh [C.J. Earle, 2004.10.23].
Sapling, about 130 cm tall, in the above stand [C.J. Earle, 2004.10.23].
Open-grown tree along the Blue Ridge Parkway in North Carolina [C.J. Earle, 2004.10.26].
Cone, Uwharrie National Forest, North Carolina. The prickle length is variable - this cone has rather long prickles, perhaps related to the fact that it grew on a stunted tree on ultramafic soil [C.J. Earle, 2004.10.23].
Bark on a tree about 30 cm dbh, Uwharrie National Forest, North Carolina [C.J. Earle, 2004.10.23].
Twig and foliage from a tree at Linville Gorge, North Carolina [C.J. Earle, 2004.10.27].
Range map, redrawn from Carter and Snow (1990). Also take a look at this offsite range map ( Prasad and Iverson 1999 )
Pinus virginiana Miller 1768 Common namesVirginia pine, scrub pine, spruce pine, Jersey pine (Carter and Snow 1990). Taxonomic notesSyn.: Pinus inops Aiton 1789; Pinus turbinata Bosc ex Loudon 1842 ( Farjon 1998 ). This species belongs to subgenus Pinus , section Contortae , which consists of four closely related North American two-needled pines. Experimental crosses have succeeded in hybridizing P. virginiana with only one of these four, Pinus clausa (Carter and Snow 1990). The four species of section Contortae have done an admirable job of dividing up the available terrain; Pinus clausa occupies poor soils on fire-prone sites in the hot southeastern U.S., P. virginiana does the same thing in the temperate regions of the eastern U.S.; P. banksiana carries the torch high into the boreal forest; and P. contorta with its three subspecies does the same thing across western North America from Baja to Yukon. DescriptionMonoecious evergreen trees 9-18(-32) m tall and 30-50(-83) cm dbh. Straight to contorted with usually a single round trunk and an irregular crown of long, spreading, ascending to descending branches. Bark smooth, then reddish, scaly, finally gray-brown, thick, shaggy. Branchlets slender, reddish or purplish, often glaucous, aging red-brown to gray, rough. Foliar buds ovoid to cylindric, red-brown, 0.6-1cm, sometimes resinous; scale margins white, fringed. Needles 2 per fascicle, (2-)4-8 cm × 1-1.5 mm, twisted, deep to pale yellow-green, all surfaces with inconspicuous stomatal lines, margins serrulate, apex narrowly acute; sheath 0.4-1cm, persistent; needles live 3-4 years. Pollen cones ellipsoid-cylindric, 10-20 mm, red-brown or yellow. Seed cones borne throughout the tree's crown and persisting for up to 5 years; symmetrical, narrowly ovoid, when open, (3-)4-7(-8) cm long, red-brown, nearly sessile or on stalks to 1 cm, scales rigid, with strong purple-red or purple-brown border on adaxial surface distally; apophyses slightly thickened, slightly elongate; umbo central, low-pyramidal, with slender, stiff prickle. Seeds 4-7 mm, compressed-obovoid, mottled brown, with a narrow wing up to 20 mm long. 2 n =24" ( Little 1980 , Carter and Snow 1990, Kral 1993 , and my field observations). Life History: Vegetative reproduction does not occur naturally. Pollination (by wind) occurs from mid-March to late May depending on local temperatures. Fertilization occurs 13 months later, when the cones are nearly at full size, and cones mature between late September and early November. Seed disperse shortly thereafter, although cones typically remain on the tree for several (up to 15) years. Some cones mature every year, with mast crops about every 3 years. Seedlings require an exposed mineral soil seedbed and direct sunlight, and are relatively drought-tolerant compared to most pine seedlings. In favorable conditions seedlings may be 10-20 cm tall after the first year and 5 m tall after 10 years, reaching maturity after about 60 years; cone production may begin as early as 5 years or as late as 50 depending on stocking and other factors. Mortality can have many causes; among the most commonly observed are fire, windthrow, effects due to competition during succession to a hardwood forest, heart rot due to Phellinus pini , pitch canker due to Fusarium moniliforme var. subglutinans , and insect attack by pine beetle ( Dendroctonus frontalis ), sawflies ( Neodiprion spp.), and pales weevil ( Hylobius pales , attacks seedlings). Virginia pine is also sensitive to air pollutants including ozone, sulfur dioxide and nitrogen oxides (Carter and Snow 1990). RangeUSA: New York, New Jersey, Pennsylvania, Ohio, Indiana, Kentucky, Tennessee, Mississippi, Alabama, Georgia, South Carolina, North Carolina, West Virgina, Virginia, Maryland and Delaware at 0-900 m on dry uplands, sterile sandy or shaly barrens, old fields, and lower mountains ( Kral 1993 ). Naturalized in Canada: Alberta, British Columbia, and Ontario (Brouillet et al. 2006, cited by PLANTS database 2009.03.31 ). See also Thompson et al. (1999) . Precipitation within the range of this species averages 890-1400 mm, with the wettest areas in the southern portion of its range, and is fairly evenly distributed throughout the year. Summer average temperatures are 21° to 24°C and winter temperatures average -4° to 4°C. It grows best on well-drained clay, loam, or sandy loam soils with silicate parent rocks, but also grows in areas of limestone and shale; on less well-drained sites it gives way to other species such as P. taeda (Carter and Snow 1990). This species is commonly early seral, appearing in old fields or other disturbed sites and regenerating rapidly after fire. It forms a dominant cover type with various understory oaks ( Quercus sp.), and is an associated species in a variety of oak forest types as well as in some forest types dominated by Pinus rigida , P. echinata , P. taeda , P. pungens , P. palustris , P. strobus , Tsuga canadensis , or Juniperus virginiana (Carter and Snow 1990). These associations vary considerably with geography; it is associated with P. rigida and P. pungens in the Appalachian Mountains, with Pinus taeda on the eastern shores of Virginia and Maryland, and with P. echinata in the Piedmont region ( FEIS database ). The following remarks on fire ecology of Virginia pine are quoted from the FEIS database : Virginia pine is not well adapted to survive fire due to thin bark and shallow roots. Large trees however, are apparently able to survive fires. Virginia pine stands that include six size classes (d.b.h) have been documented. This size distribution is apparently due to fires that burned at approximately 20- to 30-year intervals. The larger trees, therefore, survived at least one fire. Virginia pine populations are maintained by fire or other disturbance; Virginia pine is a colonizer of recently burned sites. Root crown sprouts have been reported, but are apparently not an important fire survival mechanism. Fire regimes in habitats containing Virginia pine have been altered by humans for many years. It is thought that prior to European settlement, Indians maintained large tracts of pine forests through intentional burning of forest lands for various purposes (e.g., agriculture, wildlife harvest). These fires created a patchwork of communities, increasing the amount of area covered by pioneer or pyrophytic species such as Virginia and pitch pines. Currently, lightning fires do occur, but are of low importance compared to those started by people. Landers estimated the fire return interval in the southeastern United States at approximately 2 fires of high intensity per 100 years. In the Great Smoky Mountains National Park, Tennesee and South Carolina, fire intervals for 1856 to 1900 and for 1900 to 1940 were both estimated to be 9.2 years below 2,000 feet (610 m) elevation, and 11.3 years above that elevation. Big treeDiameter 83 cm, height 31 m, crown spread 15 m, located in Madisonville, KY ( American Forests 1996 ). The tallest known one is in Great Smoky Mountains National Park; it is 33.83 m tall ( Rucker 2003 ). OldestThe species is said to become senescent at ages of 65 to 90 years, and to rarely live more than 150 years ( FEIS database ). I have not been able to locate more detailed information, but based on having seen it growing on dry rocky outcrops in places like Linville Gorge, I would expect that such sites would yield older trees. DendrochronologyThere is no record of dendrochronological use of this species. EthnobotanyThe Cherokee used this species medicinally, for a startling array of ailments including (Hamel and Chiltoskey 1975):
and also for the following purposes:
Economically, Virginia pine was historically used for mine timbers, railroad ties, rough lumber, fuel, tar, and charcoal. Currently it is primarily grown for pulpuse as a pulp, especially through the reforestation of abandoned agricultural lands, cutover, and mined sites. It is widely planted in the middle and southern Appalachian region during revegetation of surface coal mine spoils ( FEIS database ). ObservationsThe species can be easily found throughout most of its range, and indeed is the predominant pine on dry sites at low to moderate elevations. Among other places, it occurs in Shenandoah National Park , Mammoth Cave National Park and Great Smoky Mountains National Park . RemarksVirginia pine seeds are an important food source for many small mammals and birds. Older trees that have begun to suffer stem rot provide good nesting sites for woodpeckers. When used for revegetation of mine spoils, Virginia pine has high value for wildlife cover and food, and is locally very important for foraging white-tailed deer ( FEIS database ). CitationsBrouillet, L., F. Coursol, and M. Favreau. 2006. VASCAN. The database of Canadian vascular plants. Herbier Marie-Victorin, Institut de recherche en biologie végétale, Université de Montréal. Carter, K.K. and A.G. Snow Jr. 1990. Pinus virginiana Mill., Virginia Pine. Pp. 513-519 in Burns and Honkala . Hamel, Paul B. and Mary U. Chiltoskey. 1975. Cherokee Plants and Their Uses -- A 400 Year History . Sylva, N.C.: Herald Publishing Co. See alsoPinus virginiana Mill., Virginia pine - Biodiversity of Great Smoky Mountains National Park , accessed 2009.03.28. Recommended!
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Edited by Christopher J. Earle Page updated on 2009.03.31
URL: http://www.conifers.org/pi/pin/virginiana.htm |
| Following modified from Plants Database, United States Department of Agriculture |
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| Following served from Brooklyn Botanical Garden |
| Following modified from Uni-bonn |
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| Following modified from Virginia Tech Forestry Department |
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| Following modified from US Forest Service |
Pinus virginiana Mill. Virginia Pine Pinaceae -- Pine family Katherine K. Carter and Albert G. Snow, Jr. Virginia pine (Pinus virginiana) has a definite place among trees of commercial importance in spite of once being considered a "forest weed" and called scrub pine. Also known as Jersey pine and spruce pine, it does so well in reforesting abandoned and cutover lands that it has become a principal source of pulpwood and lumber in the southeast. Virginia pine is commonly a small or medium-sized tree but a record tree has been measured with 81 cm (31.8 in) in d.b.h. and 34.7 m (114 ft) in height. HabitatNative RangeVirginia pine generally grows throughout the Piedmont and at lower elevations in the mountains from central Pennsylvania southwestward to northeastern Mississippi, Alabama, and northern Georgia. It is also found in the Atlantic Coastal Plain as far north as New Jersey and Long Island, NY, and extends westward in scattered areas into Ohio, southern Indiana, and Tennessee.
ClimateThe annual precipitation in the native range of Virginia pine averages 890 to 1400 mm (35 to 55 in) and is fairly well distributed throughout the year. Rainfall generally is greatest in the southwestern portion of the range. The climate throughout most of this area is classified as humid. Summer temperatures average about 21° to 24° C (70° to 75° F); winter temperatures range from -4° to 4° C (25° to 40° F); and the average number of frost-free days varies from more than 225 on the eastern and southern edge of the Piedmont to 160 days on the more mountainous areas to the west and north. Soils and TopographyVirginia pine grows well on a variety of soils derived from marine deposits, from crystalline rocks, sandstones, and shales, and from limestone to a lesser extent. These are classified as Spodosols and Inceptisols. After harvesting or fire, these soils are subject to moderate sheet and gully erosion; erosion can become severe on shale soils. On many areas that now support Virginia pine, much of the A horizon is gone because of past erosion under intensive agricultural use. The species grows best on clay, loam, or sandy loam; it generally does poorly on serpentine soils, shallow shaly soils, and very sandy soils. It thrives only in moderately well drained to well drained soils and is less tolerant of wet sites and impeded drainage than pitch and loblolly pines (Pinus rigida and P. taeda). Virginia pine generally tolerates soil acidities ranging from pH 4.6 to 7.9 (39). Soil beneath a Virginia pine stand was more acidic and contained more organic matter than soil under shortleaf (P. echinata), loblolly, or white (P. strobus) pine stands (30). Virginia pine usually is found at elevations of 15 to 760 m (50 to 2,500 ft). It comes in freely on abandoned farmland throughout its range. Associated Forest CoverVirginia pine often grows in pure stands, usually as a pioneer species on old fields, burned areas, or other disturbed sites. It is a major species in the forest cover types Virginia Pine-Oak (Society of American Foresters Type 78) and Virginia Pine (Type 79) (17). It is an associate in the following cover types: Post Oak-Blackjack Oak (Type 40), Bear Oak (Type 43), Chestnut Oak (Type 44), White Oak-Black Oak-Northern Red Oak (Type 52), Pitch Pine (Type 45), Eastern Redcedar (Type 46), Shortleaf Pine (Type 75), Loblolly Pine (Type 81), and Loblolly Pine-Hardwood (Type 82). Other than those named in the types, species that commonly grow with Virginia pine in various parts of its range are white oak Quercus alba), southern red oak (Q. falcata), red maple (Acer rubrum), hickories (Carya spp. ), blackgum (Nyssa sylvatica), sweetgum (Liquidambar styraciflua), eastern hemlock (Tsuga canadensis), Table Mountain pine (Pinus pungens), and eastern white pine (P. strobus). In central Pennsylvania, two ground-cover types serve as indicators of site quality for Virginia pine. The flowering dogwood/clubmoss (Cornus florida / Lycopodium) type indicates the better site indexes ranging from 15.2 to 21.3 m (50 to 70 ft); the bear oak/reindeer moss (Quercus ilicifolia / Cladonia) type indicates average and poor site indexes between 9.1 to 15.2 m (30 and 50 ft) (39). Life HistoryReproduction and Early GrowthFlowering and Fruiting- Virginia pine is monoecious. Pollen shedding and female cone receptivity begin about the middle of March in the southern part of the species range, and as late as the latter part of May in the northern part. Virginia pine is wind pollinated and primarily outcrossing, though self-fertilization is possible. Fertilization takes place in early June some 13 months later, when the cones have nearly reached full size. Seeds become viable by middle to late August of the year after pollination but are difficult to extract before cone maturation, which occurs from late September to early November. Unlike many other pines, Virginia pine produces cones in all parts of the crown. Empty cones usually persist on the tree for several years and can remain for as many as 15 years. Seed Production and Dissemination- Open-grown trees often produce cones as early as 5 years of age, and a few trees have been known to flower at 18 months (3). In dense stands, cone production can be delayed for as many as 50 years. As stands become more open, cone production is accelerated (36). Virginia pine produces some seed each year, with heavy cone crops occurring at intervals of 3 or more years. Good cone crops can be produced in 2 successive years, however, and peak seed years do not necessarily coincide throughout the range. Early cone production is under strong genetic control and can be increased by family selection or fertilization (7,9). Seed dispersal starts in October and is complete within 3 months, though some seeds may continue to be released until the following spring. Most of the seeds fall within 30 m (100 ft) of trees with an average height of 18 m (60 ft); however, stocking often is adequate at greater distances, particularly on the lee side of a seed source. In the coastal plain of Maryland, seedfall was measured on a 40-meter-wide (132 ft) strip cut through Virginia pine. Over a 4-year period, seedfall per hectare ranged from 15,800 to 98,800 (6,400 to 40,000/acre) (18). The number of clean seeds per kilogram ranges from 100,750 to 200,800 (45,700 to 91,100/lb); the average is 122,100 (55,400/lb) (35). Seed and cone insects can severely reduce the yield of viable seed. Seed yields from cones from which insects were excluded by wire screens were twice as high as those from unprotected cones (8). Major insect pests are two types of seedbugs: the shieldbacked pine seedbug (Tetyra bipunctata) and the southern pine seedbug (Leptoglossus corculus). Several types of coneworms (Dioryctria spp. ) and cone borers (Eucosma spp. ) also infect Virginia pine. The Virginia pine sawfly (Neodiprion pratti pratti) and Nantucket pine tip moth (Rhyacionia frustrana) can destroy young conelets (16). Seedling Development- An exposed mineral soil seedbed is essential for successful establishment of seedlings. In one study area in the southern Appalachians, all regeneration of Virginia pine over a 120-year period was related to site disturbances by fires or logging (1). Such site disturbance can result in two to four times as much germination as on undisturbed seedbeds, and 2-year survival that is four times as great (41). Exposing wet Virginia pine seeds to artificial light before sowing greatly increases germination. Maximum germination is obtained by exposing seeds that have been soaked in water for 24 hours to 30 minutes of red light. The stimulus to germination by this exposure can be reversed by treatment with far-red light (39). Germination is epigeal (35). Seedlings require direct sunlight for best growth. Even partial shade reduces growth, and seedlings do not survive under full shade. Given adequate light and a good seedbed, however, several thousand seedlings per hectare can become established. Precommercial thinning at age 5 has been recommended to prevent stagnation in heavily stocked seedling stands (11). Virginia pine seedlings grown in containers in the greenhouse can be used to advance growth and cone production by 1 year compared to the use of bare-root stock (6). Extra light from an incandescent source coupled with a high level of nutrition can quadruple height growth in one season. Long photoperiods also induce other effects such as increased internodal length, accelerated cycles of bud formation, and breaking of bud dormancy (39). The balance and relative abundance of inorganic elements in the soil solution also are important to the establishment and growth of Virginia pine. In basic nutrition studies in irrigated sand cultures, symptoms of deficiency appeared when either potassium or magnesium was supplied at 0.01 milliequivalent (meq) or less per liter. Amounts adequate for healthy height growth were 0.35 meq of calcium and 2 meq of magnesium per liter. The adequacy level for potassium was between 0.1 and 1 meq; the minimum levels for nitrogen and phosphorus were 1.78 and 0.03 meq, respectively (39). Virginia pine seedlings are more tolerant of low soil moisture than most other pines. Although they may survive when moisture is low, their rate of growth is slower on dry sites. Seedlings reach a height of 10 to 20 cm (4 to 8 in) in the first year when growth conditions are favorable. At the end of 10 years, the average height may reach 5 m (17 ft) on the better sites. Many species of mycorrhizae representing nine genera (Amanita, Boletus, Cenococcum, Gomphidius, Lepiota, Paxillus, Rhizopogon, Russula, and Scleroderma) are known to form associations with the roots of Virginia pine (23). Vegetative Reproduction- Sprout growth on Virginia pine is rare. Occasionally, cut stubs produce a few short-lived sprouts from dormant buds. Rooting of cuttings from 7- and 8-year-old Virginia pine is most successful (72 percent rooted) when cuttings were taken in December and treated with 0.2 percent indolebutyric acid before being placed in a mist chamber (40). Cuttings from 1-year-old seedlings also can be rooted, but those taken from mature trees fail to root (25). Grafting generally is about 65 percent successful when dormant scions are grafted onto dormant rootstock. The side-veneer graft technique is most commonly used, but other methods also are successful. Virginia pine grafts are more susceptible to mold than grafts of the other southern pines (25). Clonal plantlets can be obtained from tissue cultures when cotyledons from Virginia pine embryos are used. However, the rooting techniques necessary for commercial production of these plantlets have not yet been developed (10). Sapling and Pole Stages to MaturityGrowth and Yield- On average sites, well-stocked stands can have as many as 3,950 stems per hectare (1,600/acre) at 20 years of age. The number drops to about 500/ha (200/acre) in 70-year-old stands. The site index for Virginia pine is the average height of dominant trees measured at age 50 years. In North Carolina, the average merchantable volume per hectare for site index 18.2 m (60 ft) land is 112 m³ (1,600 ft³/acre) at 20 years and 354 m³ (5,050 ft³/acre) at 70 years (36). Volumes for Maryland are intermediate between the higher values for North Carolina and the lower values for Pennsylvania. In a regional study extending from Maryland to South Carolina, merchantable volumes per hectare for fully stocked, pure, 60-year-old stands ranged from 155 m³/ha (2,210 ft³/acre) for site index 16.8 m (55 ft) land to 602 m³/ha (8,600 ft³/acre) for site index 24.4 m (80 ft) land (31). On the best sites, trees can reach a height of 37 m (120 ft) at maturity, but the average height ranges from 15 to 23 m (50 to 75 ft) at age 50. An annual growth rate of 6 m³/ha (1 cord/acre) is possible over a large portion of its natural range. Because Virginia pine is shallow rooted and subject to windthrow and to damage from ice and snow, thinning is not recommended in older stands. In one thinned 17-year-old stand the diameter growth of trees was 50 percent greater than that of controls; however, there was no overall stand response because of frequent windthrow in the thinned stand. Windthrow is not serious in younger stands, which can be thinned safely, but the growth response in these stands may not be sufficient to replace the volume removed by the thinning (19). Virginia pine planted on old fields grows well. One plantation in Iowa had a mean annual height growth of 0.6 m (1.9 ft) after 15 years. This growth was better than that of five other pine species planted on the same sites. The mean annual diameter growth was 8.6 mm (0.34 in) during the same period (39). Plantations in the Cross Timbers area of Oklahoma survived well when moisture was adequate during the year of establishment (32). In the Cumberland Plateau, planted Virginia pine on site index 21.2 m (70 ft) produced a merchantable volume of approximately 140 m³/ha (2,000 ft³/acre) at age 20 (37). In central Tennessee, Virginia pine outperforms shortleaf and loblolly pines on dry ridges and on warm slopes with shallow soil (38). On these sites it is estimated to produce approximately 56 m³ more per hectare (800 ft³ or 4,000 fbm/acre) than shortleaf pine, on a 50-year rotation (22). On good sites in the Piedmont or on cove sites in the southern Appalachians, however, growth of Virginia pine is inferior to the other southern pines. Natural pruning in Virginia pine is slow because the branches are resinous. Rooting Habit- Virginia pine is a shallow-rooted species and losses from windthrow are likely to occur if old stands are thinned excessively (5). Reaction to Competition- Being intolerant of shade, Virginia pine is a transitional type and is eventually replaced by more tolerant hardwood species. It is a pioneer species, coming in after fire, and on eroded areas or wornout old fields. Compared with associated pines, it is generally more successful on poorer sites. Virginia pine seedlings cannot become established under the shade of an existing stand, so hardwoods invade the understory. These hardwoods become dominant and gradually take over the area in succeeding generations, unless fire or other factors retard them (39). Damaging Agents- Heart rot due to Phellinus pini often is present in stands more than 60 years old, but it is rare in stands less than 50 years of age. In a severe case, as much as 34 percent of the trees in a 59-year-old stand were infected (36). Partly because of its susceptibility to heart rot, pulpwood rotations generally are preferred to sawtimber rotations in Virginia pine. The other serious disease of Virginia pine is pitch canker (Fusarium moniliforme var. subglutinans), which enters twigs or stems through small wounds and causes a heavy exudation of pitch. The canker enlarges rapidly and eventually girdles the twig or stem. Seedlings infected with pitch canker have a mortality rate of about 90 percent (15). Some variation in susceptibility to pitch canker appears to have a genetic basis (2). Other diseases usually cause little loss of growth in Virginia pine. Stem cankers (Atropellis tingens), eastern gall rust (Cronartium quercuum), a stem rust (C. comptoniae), root rot (Heterobasidion annosum), and butt rots (Poria subacida, Phaeolus schweinitizii) occasionally infest Virginia pine. The principal forest insects that cause significant damage to Virginia pine are the southern pine beetle (Dendroctonus frontalis), Ips spp. , and pine sawflies, the Virginia pine sawfly (Neodiprion pratti pratti) and the redheaded pine sawfly (N. lecontei). Trees under stress of lightning, fire, or logging injury are more susceptible to insect attack than sound healthy trees (39). The pales weevil (Hylobius pales), which feeds on and often kills small seedlings of several pine species, can greatly reduce the regeneration of Virginia pine. Attacks are most likely on recently cutover areas where pine roots provide the food needed to build up a large larval population. Girdling by meadow mice can cause considerable damage in young trees. In Tennessee, they have reportedly caused heavy mortality in 8- or 9-year-old plantations (26). In Maryland and Iowa, they have shown a strong preference for Virginia pine over other pine species (39). Young Virginia pines are particularly vulnerable to fire because of their thin bark and their lack of long-lived dormant buds at the base, along the bole, and in the crown. Fire reduces the Virginia pine component in stands where this species is mixed with pitch, shortleaf, or loblolly pines. The species also is sensitive to several air pollutants. Of 18 pine species tested, Virginia pine was most sensitive to ozone; 69 percent of the seedlings suffered foliar damage. Polluted air containing sulfur dioxide and oxides of nitrogen also reduced terminal growth, with most damage occurring between the 4th and 13th weeks after budbreak. Dormant seedlings are resistant to ozone pollution (14,33). Special UsesOf the southern conifers, Virginia pine is most preferred as a Christmas tree. If families with desirable traits are selected and appropriate cultural practices are used, marketable Christmas trees can be produced in as few as 3 years, although the usual rotation age for Virginia pine Christmas trees is 5 to 10 years (4,24). In the Eastern and Central States, Virginia pine performs well when planted on strip-mined sites. In a study in West Virginia, Virginia pine survived well, grew quickly, and encountered no serious pests 14 years after being planted on a mined site (43). It is also a satisfactory species for the reclamation of spoil banks in the Southeast (27). Because the wood of older trees is frequently softened by fungal decay, Virginia pine provides nesting habitat for woodpeckers. Leaving old, decayed trees near the margins of clearcuts provides nesting sites (13). GeneticsPopulation DifferencesMost of the variation in Virginia pine is attributable to differences among individual trees or stands rather than to geographic origin, though it is suspected that populations in the Talladega Mountains of central Alabama and on the deep sands of the mid-Atlantic Coast are distinct ecotypes (25). A range-wide sample of 2,114 trees revealed no evidence of north-south or east-west trends in specific gravity (unextracted wood) (12). In studies of six wood properties of mature Virginia pine in Kentucky and Tennessee, variation usually was greater within a stand than among stands. However, tracheid length increased from south to north within this region (42). Progeny tests of trees from the same locations also revealed significant variation in monoterpene content and in stem volume at age 5. This variation was attributable to difference among stands and among individual trees within stands (29,34). These and other progeny tests indicate that tree improvement programs for Virginia pine can significantly improve the stem form and growth rate. Seeds from local sources or from locations with a climate similar to that of the planting site generally produce trees with the best survival and growth rates. Seed from southern provenances produce fast-growing trees on southern sites, but southern trees grow slowly and suffer winter injury when planted in the north (20,21). HybridsHybrids of Virginia pine and Ocala sand pine (Pinus clausa var. clausa) can be made under controlled conditions with either species as the seed parent. Controlled crosses of P. virginiana with jack pine (P. banksiana) and lodgepole pine (P. contorta) have not been successful (25). Literature Cited
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| Following modified from Plants Database, United States Department of Agriculture |
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